UNIVERSITI PUTRA MALAYSIA UTILIZATION OF BIOMASS …psasir.upm.edu.my/id/eprint/70185/1/FBSB 2017 14...

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UNIVERSITI PUTRA MALAYSIA UTILIZATION OF BIOMASS-DERIVED ACTIVATED CARBON AS CATALYST SUPPORT AND BIOADSORBENT IN BIODIESEL PRODUCTION USING WASTE COOKING OIL AS FEEDSTOCK MOHAMMED ABDILLAH BIN AHMAD FARID FBSB 2017 14

Transcript of UNIVERSITI PUTRA MALAYSIA UTILIZATION OF BIOMASS …psasir.upm.edu.my/id/eprint/70185/1/FBSB 2017 14...

UNIVERSITI PUTRA MALAYSIA

UTILIZATION OF BIOMASS-DERIVED ACTIVATED CARBON AS CATALYST SUPPORT AND BIOADSORBENT IN BIODIESEL

PRODUCTION USING WASTE COOKING OIL AS FEEDSTOCK

MOHAMMED ABDILLAH BIN AHMAD FARID

FBSB 2017 14

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CATALYST SUPPORT AND BIOADSORBENT IN BIODIESEL PRODUCTION USING WASTE COOKING OIL AS FEEDSTOCK

By

MOHAMMED ABDILLAH BIN AHMAD FARID

Thesis Submitted to the School of Graduate Studies, Universiti Putra Malaysia, in Fulfilment of the Requirement for Degree of Master of Science

April 2017

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All material contained within the thesis, including without limitation text, logos, icons, photographs and all other artwork, is copyright material of Universiti Putra Malaysia unless otherwise stated. Use may be made of any material contained within the thesis for non-commercial purposes from the copyright holder. Commercial use of material may only be made with the express, prior, written permission of Universiti Putra Malaysia.

Copyright © Universiti Putra Malaysia

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Abstract of thesis presented to the Senate of Universiti Putra Malaysia in fulfilment of the requirement for the degree of Master of Science

UTILIZATION OF BIOMASS-DERIVED ACTIVATED CARBON AS CATALYST SUPPORT AND BIOADSORBENT IN BIODIESEL

PRODUCTION USING WASTE COOKING OIL AS FEEDSTOCK

By

MOHAMMED ABDILLAH BIN AHMAD FARID

April 2017

Supervisor : Mohd Ali Hassan, PhD Faculty : Biotechnology and Biomolecular Sciences

The depletion of non-renewable fossil fuels and the growing environmental awareness, biodiesel is seen as a promising substitute for the conventional diesel. Its eco-friendly properties such as being renewable, biodegradable and less carbon emission have brought new hope for a greener future. Presently, waste cooking oil and oil palm empty fruit bunch were extensively used as the raw materials for a low-cost feedstock and catalyst for biodiesel production. Apart from its economic objective, exploitation of these abundant waste sources for biodiesel production is a step ahead in saving the environment from pollution, as it is typically being disposed indiscriminately.

In this study, improved production of biodiesel from waste cooking oil was achieved by using a newly developed potassium phosphate tri-basic supported activated carbon catalyst. In order to produce high surface area activated carbon, press-shredded oil palm empty fruit bunch was subjected to carbonization at 700ᴼC for 2 h followed by activation with potassium hydroxide at 700ᴼC for 2 h. To produce the catalyst, calcination was performed at different potassium phosphate tri-basic impregnation concentrations (1:0.25 to 1:1 activated carbon to potassium phosphate tri-basic weight ratio) and temperatures (400ᴼC to 700ᴼC). Prior to transesterification, waste cooking oil was analysed for its physicochemical properties and pre-treated to remove moisture and residues. Under the optimum condition of 5 wt% catalyst loading, 12:1 methanol to oil molar ratio at 60ᴼC for 4 h, 98% of biodiesel yield was achieved, which surpassed the European Biodiesel Standard (EN 14214). The catalyst was reusable for 5 successive reaction cycles, achieving almost 80% of biodiesel yield.

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In addition, the activated carbon produced from the press-shredded oil palm empty fruit bunch was also utilized as bioadsorbent to remove impurities from the crude biodiesel. The purification process was performed using different adsorbent loadings (1 to 5 wt%) under continuous stirring condition at 500 rpm for 1 h. Approximately 89.71% of methanol, 81.74% of water, 36.67% of FFA and 98.61% of potassium (K) were successfully removed after purification at 5 wt% of bioadsorbent loading, which met the European Biodiesel Standards (EN 14214). In comparison to other commercial adsorbents and conventional water washing method, purification using the biomass-derived bioadsorbent resulted in better removal of methanol, water and triglyceride impurities with only a small loss of biodiesel yield.

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Abstrak tesis yang dikemukakan kepada Senat Universiti Putra Malaysia sebagai memenuhi keperluan untuk ijazah Master Sains

PENGGUNAAN KARBON TERAKTIF DIPEROLEH DARIPADA BIOJISIM SEBAGAI PENYOKONG PEMANGKIN DAN BIO-PENJERAP DIDALAM PENGHASILAN BIODIESEL MENGGUNAKAN SISA MINYAK MASAK

SEBAGAI BAHAN MENTAH

Oleh

MOHAMMED ABDILLAH BIN AHMAD FARID

April 2017

Penyelia : Mohd Ali Hassan, PhD Fakulti : Bioteknologi dan Sains Biomolekul

Dengan pengurangan bahan api fosil yang tidak boleh diperbaharui dan kesedaran alam sekitar yang semakin meningkat, biodiesel dilihat sebagai pengganti yang memberangsangkan untuk diesel konvensional. Ciri-ciri mesra alam seperti boleh diperbaharui, biodegradasi dan kurang pelepasan karbon telah membawa harapan baru untuk masa depan yang lebih hijau. Kini, sisa minyak masak telah digunakan dengan meluas sebagai bahan mentah dan pemangkin bagi pengeluaran biodiesel kos rendah. Selain daripada objektif ekonomi, eksploitasi sumber sisa yang banyak ini bagi pengeluaran biodiesel adalah satu langkah ke hadapan dalam menyelamatkan alam sekitar daripada pencemaran dan penyumbatan sistem kumbahan sanitari, kerana ia biasanya dilupuskan secara sewenang-wenangnya.

Dalam kajian ini, peningkatan pengeluaran biodiesel daripada sisa minyak masak telah dicapai dengan menggunakan pemangkin potassium fosfat tri-asas disokong karbon teraktif. Dalam usaha untuk menghasilkan luas permukaan karbon teraktif yang tinggi, tandan kelapa sawit kosong ditekan-cincang telah dikarbonisasi pada suhu 700ᴼCselama 2 jam diikuti oleh pengaktifan dengan kalium hidroksida pada 700ᴼC selama 2 jam. Pengkalsinan dilakukan pada kepekatan impregnasi kalium fosfat tri-asas (1: 0.25 kepada 1: 1 diaktifkan karbon kalium fosfat nisbah berat tri-asas kepada) dan suhu (400ᴼC untuk 700ᴼC) yang berbeza. Sebelum transesterifikasi, sifat fizikokimia sisa minyak masak telah dianalisis dan dipra-rawat untuk membuang kelembapan dan residu. Di bawah keadaan optimum 5% berat unit muatan pemangkin, 12:1 nisbah

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molar metanol kepada sisa minyak masak pada 60ᴼC untuk bagi 4 jam, 98% hasil biodiesel telah dicapai, yang melepasi Piawaian Biodiesel Eropah (EN 14214). Pemangkin ini boleh diguna semula untuk 5 kitaran reaksi berturut-turut, mencapai hampir 80% hasil biodiesel.

Di samping itu, karbon teraktif yang dihasilkan daripada tandan kelapa sawit kosong yang ditekan-cincang juga digunakan sebagai bio-penjerap untuk membuang kekotoran daripada biodiesel mentah seperti air, asid lemak bebas (FFA), metanol, gliserin bebas, trigliserida dan kalium. Proses penulenan biodiesel mentah yang dihasilkan daripada sisa minyak masak telah dilakukan dengan menggunakan muatan penjerap yang berbeza (1 hingga 5% berat unit) di bawah keadaan kacau berterusan pada 500 rpm selama 1 jam. Kira-kira 89.71% metanol, 81.74% air, 36.67% FFA and 98.6% kalium telah berjaya dibuang selepas penulenan pada 5% berat unit muatan bio-penjerap, yang mana telah melepasi Piawaian Biodiesel Eropah (EN 14214). Berbanding dengan penjerap komersial yang lain dan kaedah konventional basuhan air, penulenan menggunakan bio-penjerap yang diperolehi daripada biojisim telah mengakibatkan penyingkiran metanol, air dan trigliserida yang lebih baik dengan kehilangan hasil biodiesel yang kecil.

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ACKNOWLEDGEMENTS

“In The Name of Allah, the Most Gracious and Most Merciful”

First of all, praise to ALLAH SWT for the opportunity given in facing all the difficulties during my research.

Words cannot express my gratitude towards my supervisor Prof. Dr. Mohd Ali Hassan, who has been my advisor for guidance in this thesis research. Also, I would like to heartily thank my co-supervisors Prof. Dr. Yoshihito Shirai and Prof. Dr. Taufiq Yap Yun Hin who gave me the knowledge, advice and generous suggestions throughout my research work.

To all other members of Biomass Technology Center lab, I would like to express my gratitude and thankfulness for creating such a friendly working atmosphere and all the useful discussions.

Finally, this special gratefulness goes to my parents and my siblings. This research work and thesis writing would not complete without their support and encouragement continuously from the beginning until the successful completion.

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This thesis was submitted to the Senate of Universiti Putra Malaysia and has been accepted as fulfillment of the requirement for the degree of Master of Science. The members of the Supervisory Committee were as follows:

Mohd Ali Hassan, PhD Professor Faculty of Biotechnology and Biomolecular Sciences Universiti Putra Malaysia (Chairman)

Taufiq Yap Yun Hin, PhD Professor Faculty of Science, University Putra Malaysia (Member)

Yoshihito Shirai, PhD Professor Graduate School of Life Sciences and System Engineering Kyushu Institute of Technology (Member)

_________________________ ROBIAH BINTI YUNUS, PhD Professor and Dean School of Graduate Studies Universiti Putra Malaysia

Date:

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Declaration by graduate student

I hereby confirm that:

� This thesis is my original work; � Quotations, illustrations and citations have been duly referenced; � This thesis has not been submitted previously or concurrently for any other degree

at any other institutions; � Intellectual property from the thesis and copyright of thesis are fully owned by

Universiti Putra Malaysia, as according to the Universiti Putra Malaysia (Research) Rules 2012;

� Written permission must be obtained from supervisor and the office of Deputy Vice-Chancellor (Research and Innovation) before thesis is published (in the form of written, printed or in electronic form) including books, journals, modules, proceedings, popular writings, seminar papers, manuscripts, posters, reports, lecture notes, learning modules or any other materials as stated in the Universiti Putra Malaysia (Research) Rules 2012;

� There is no plagiarism or data falsification/fabrication in the thesis, and scholarly integrity is upheld as according to the Universiti Putra Malaysia (Graduate Studies) Rules 2003 (Revision 2012-2013) and the Universiti Putra Malaysia (Research) Rules 2012. The thesis has undergone plagiarism detection software.

Signature: ____________________________ Date: _________________

Name and Matric No.: Mohammed Abdillah Bin Ahmad Farid (GS37941)

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Declaration by Members of Supervisory Committee

This is to confirm that:

� The research conducted and the writing of this thesis was under our supervision; � Supervision responsibilities as stated in the Universiti Putra Malaysia (Graduate

Studies) Rules 2003 (Revision 2012-2013) are adhered to.

Signature: ___________________________ Name of Chairman of Supervisory Committee: Prof. Dr. Mohd Ali Hassan

Signature: __________________________ Name of Member of Supervisory Committee: Prof. Dr. Taufiq Yap Yun Hin

Signature: __________________________ Name of Member of Supervisory Committee: Prof. Dr. Yoshihito Shirai

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TABLE OF CONTENTSPage

ABSTRACT i

ABSTRAK iii

ACKNOWLEDGEMENTS v

APPROVAL vi

DECLARATION viii

LIST OF TABLES xiv

LIST OF FIGURES xv

LIST OF ABBREVATIONS xvii

CHAPTER

1 INTRODUCTION1.1 General introduction 1

1.2 Problem statement 1

1.3 Specific objectives 3

1.4 Experimental overview 3

2 LITERATURE REVIEW2.1 Oil palm biomass waste 5

2.1.1 Oil Palm Empty fruit bunch (OPEFB) 5

2.2 Activated carbon produced from oil palm empty fruit bunch (OPEFB)

6

2.3 Biodiesel 9

2.4 Biodiesel feedstocks 9

2.4.1 Waste cooking oil (WCO) 10

2.4.2 Properties of waste cooking oil (WCO) 10

2.5 Biodiesel production methods 11

2.5.1 Transesterification 11

2.5.2 Esterification 14

2.6 Variables affecting in biodiesel production 15

2.6.1 Reaction temperature 15

2.6.2 Reaction time 15

2.6.3 Molar ratio of alcohol to oil feedstock 15

2.6.4 Free fatty acid (FFA) 16

2.6.5 Moisture content 16

2.6.6 Types of catalyst 16

2.6.6.1 Homogeneous catalyst 18

2.6.6.2 Heterogeneous catalyst 20

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2.6.6.2.1 Carbon supported catalyst

21

2.7 Biodiesel Purification 25

2.7.1 Water-washing purification method 26

2.7.2 Dry purification using adsorbents 27

2.7.2.1 Biodiesel purification using activated carbon

28

2.7.2.2 Biodiesel purification using silica gel

28

2.7.2.3 Biodiesel purification using bentonite

29

2.7.2.4 Biodiesel purification using talc 29

2.8 Biodiesel Quality Standards 29

3 BIODIESEL PRODUCTION FROM WASTE COOKING OIL USING HETEROGENEOUS BIOMASS-BASED CATALYST3.1 Introduction 32

3.2 Materials and Methods 32

3.2.1 Materials 32

3.2.2 Characterization of waste cooking oil (WCO)

33

3.2.2.1 Molecular weight of waste cooking oil (WCO)

33

3.2.3 Catalyst preparation 34

3.2.4 Catalyst characterization 36

3.2.4.1 Scanning electron microscopy (SEM) and energy-dispersive x-ray (EDX)

36

3.2.4.2 Brunauer-Emmett-Teller (BET) and Barrett-Joyner-Halenda (BJH)

37

3.2.4.3 Temperature Programmed Desorption of Carbon Dioxide (TPD-CO2)

37

3.2.4.4 X-ray diffraction (XRD) 38

3.2.4.5 Fourier transform infrared (FT-IR) spectroscopy

38

3.2.5 Preliminary treatment of oil feedstock 38

3.2.6 Transesterification 38

3.2.7 Catalyst reusability and leaching 40

3.3 Results and Discussion 40

3.3.1 Characterization of waste cooking oil (WCO)

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3.3.2 Characterization of catalyst 41

3.3.3 Transesterification reaction 46

3.3.3.1 Effect of calcination temperature

47

3.3.3.2 Effect of K3PO4 impregnation concentration

49

3.3.3.3 Effect of catalyst loading 50

3.3.3.4 Effect of methanol to oil molar ratio

50

3.3.3.5 Effect of temperature reaction 52

3.3.4 Reusability and leaching properties 53

3.4 Summary 55

4 UTILIZATION OF BIOMASS-DERIVED BIOADSORBENT IN THE PURIFICATION OF BIODIESEL PRODUCED FROM WASTE COOKING OIL4.1 Introduction 56

4.2 Materials and Methods 56

4.2.1 Materials 56

4.2.2 Molecular weight of waste cooking oil (WCO)

57

4.2.3 OPEFB-derived activated carbon production 57

4.2.4 Characterization of adsorbents 57

4.2.4.1 Scanning electron microscope (SEM)

57

4.2.4.2 Fourier transform infrared spectroscopy (FT-IR)

58

4.2.4.3 Brunauer-Emmet-Teller (BET) and energy-dispersive X-ray (EDX)

58

4.2.4.4 Methylene blue maximum adsorption capacity

58

4.2.5 Biodiesel production from waste cooking oil (WCO)

58

4.2.6 Correlation study between biodiesel impurities removal and bioadsorbent

59

4.2.7 Biodiesel purification using adsorbents 59

4.2.8 Biodiesel purification using conventional purification method

59

4.3 Results and Discussion 60

4.3.1 Characterization of crude biodiesel 60

4.3.2 Characterization of adsorbents 61

4.3.3 Correlation between adsorbent loading and biodiesel impurity removal

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4.3.4 Comparison using OPEFB- derived activated carbon with other commercial adsorbents

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4.3.5 Bioadsorbent versus water washing purification method

70

4.4 Summary 72

5 CONCLUSION AND RECOMMENDATIONS5.1 Conclusions 73

5.2 Recommendations 74

REFERENCES 75

APPENDICES 88

BIODATA OF STUDENT 96

LIST OF PUBLICATIONS 97

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LIST OF TABLES

Table Page

2.1 Comparison of activated carbon production from oil palm empty fruit bunch (OPEFB)

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2.2 Comparison of different technologies for biodiesel production

11

2.3 Homogeneous base catalysts 19

2.4 Homogeneous acid catalysts 20

2.5 Comparison of homogenously and heterogeneous catalyzed transesterification

21

2.6 Comparison of carbon supported acid catalysts 24

2.7 Effect of biodiesel impurities in engine 26

2.8 American standard specification for biodiesel (ASTM D6751)

30

2.9 European standard specifications for biodiesel (EN 14214)

31

3.1 Characterization of waste cooking oil (WCO) 41

3.2 Surface area, pore volume, average pore radius, basicity (TPD-CO2), and surface elemental distribution of OPEFB-derived activated carbon and K3PO4(1:0.25-1:1)/AC catalysts

44

3.3 FAME yield, potassium (K) and phosphorus (P) content of biodiesel product for 8 consecutive reaction cycles

54

4.1 Physicochemical properties of crude biodiesel produced from waste cooking oil (WCO)

60

4.2 Surface properties of adsorbents 63

4.3 Correlation between adsorbent loading and biodiesel impurity removal using OPEFB-derived activated carbon

66

4.4 Quality of biodiesel after purification using OPEFB-derived activated carbon and other commercial adsorbents

69

4.5 Quality of biodiesel after purification with water washing and OPEFB-derived activated carbon

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LIST OF FIGURES

Figure Page

1.1 Research work flow 4

2.1 Reaction equation of transesterification 12

2.2 Elaborate reaction equations for transesterification 12

2.3 Process flow diagram involved in biodiesel production 13

2.4 Reaction equation between alkaline catalyst and FFA 14

2.5 Reaction between acid catalyst and FFA 15

2.6 Types of catalyst for biodiesel production 17

2.7The conventional impregnation of aqueous solution between catalyst on carbon support material

23

3.1 Ground press-shredded oil palm empty fruit bunch (OPEFB) 35

3.2 Furnace equipped with nitrogen gas inlet 35

3.3 OPEFB-derived activated carbon 36

3.4One litre three-neck round-bottom flask digital heating mantle equipped with magnetic stirring and reflux condenser

39

3.5

Scanning electron micrographs of (A) K3PO4(1:1)/AC (view of capillary pores); (B) K3PO4(1:1)/AC (view of outer surface); (C) K3PO4(1:0.25)/AC (view of capillary pores); (D) K3PO4(1:0.25)/AC (view of outer surface); (E) OPEFB-derived activated carbon (view of capillary pores); and (F) OPEFB-derived activated carbon (view of outer surface)

42

3.6XRD diffractogram of OPEFB-activated carbon, K3PO4, and K3PO4(1:0.25-1:1)/AC catalysts

45

3.7FTIR spectra of OPEFB-activated carbon and K3PO4(1:0.25 -

1:1)/AC catalysts46

3.8 Thermogravimetric analysis (TGA) for the impregnated sample 48

3.9Biodiesel yield using K3PO4(1:0.75)/AC at different calcination temperatures

48

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3.10Effect of K3PO4 impregnation concentration (weight ratio of OPEFB-derived activated carbon to K3PO4 of 1:0.25 to 1:1) on biodiesel production from waste cooking oil (WCO)

49

3.11Effect of catalyst loading on biodiesel production from waste cooking oil (WCO)

50

3.12Effect of methanol to oil molar ratio on biodiesel productionfrom waste cooking oil (WCO)

51

3.13Effect of reaction temperature on biodiesel production from waste cooking oil (WCO)

52

3.14Reusability of the catalyst for 8 consecutive reaction cycles in biodiesel production from waste cooking oil (WCO)

54

4.1SEM micrographs at 300X magnification: (A) bentonite; (B) silica gel; (C) talc; and (D) OPEFB-derived activated carbon

62

4.2FT-IR spectrum of adsorbents: (A) talc; (B) silica gel; (C) OPEFB-derived activated carbon; and (D) bentonite

64

4.3Removal percentage of biodiesel impurities after purification with OPEFB-derived activated carbon at ranging adsorbent loading

67

4.4Removal percentage of biodiesel impurities after purification using OPEFB-derived activated carbon and other commercial adsorbents

69

4.5Removal percentage of biodiesel impurities after purification using conventional water washing method and OPEFB-derived activated carbon

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LIST OF ABBREVIATIONS

ASTM D6751 American biodiesel standard

BET Brunauer–Emmett–Teller

BJH Barrett-Joyner-Halenda

CH3OH Methanol

CO2 Carbon dioxide

Cu Copper

EN14214 European biodiesel standard

EDX Energy-dispersive X-ray

FAME Fatty acids methyl esters

FELDA Federal Land Development Authority

FTIR Fourier transform infrared spectroscopy

FFA Free fatty acids

GC Gas Chromatography

He Helium gas

h Hour

H2 Hydrogen gas

HCl Hydrochloride acid

K Potassium

KBr Potassium bromide

KOH Potassium hydroxide

K3PO4 Potassium phosphate tri-basic

MB Methylene blue

min Minute

M Molar

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N2 Nitrogen gas

OPEFB Oil palm empty fruit bunch

P Phosphorus

rpm Rotation per minute

SEM Scanning electron microscope

TPD Temperature Programmed Desorption

XRD X-ray Diffraction

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CHAPTER 1

INTRODUCTION

1.1 General introduction

It has been two centuries since petroleum was found and now almost 90 % of world energy supplies relied on fossil fuels (Chew & Bhatia, 2008). Nevertheless, due to its growing demand and uncontrollable consumption, the earth has begun to bear the negative consequences such as depletion of fossil fuel reserves and climate change (Adam et al., 2011). Based on the current estimate, it was expected that world fossil fuel reserves could only last for another 53 years (Xu et al., 2016). Undisputedly, the upsurge in fossil fuels utilization has increased the amount of CO2 emission which leads to global warming (Yusuf et al., 2011). Therefore, the scientific community has been intensively conducting studies to seek solutions for these issues.

Biodiesel is one of the potential biofuels that could reduce our energy dependency on fossil fuels. It consists of long-chain fatty acid alkyl esters and are normally produced from agricultural oils which are renewable (Berrios et al., 2010). It has been regarded as an alternative towards the petroleum diesel due to its better features such as low carbon emission, greater lubricity, biodegradable and less toxic (Dehkhoda et al.,2010).

1.2 Problem statement

With current technologies implemented, biodiesel production process is cost-ineffective. High price of feedstocks, non-reusable catalysts and poor downstream purification method have inevitably caused an expensive final product and costly wastewater treatment (Shu et al., 2010).

The economics of biodiesel production is strongly linked to feedstock cost, catalyst cost and wastewater treatment (Kastner et al., 2012). It has been estimated that 95% of global biofuel production uses edible oil as feedstocks (Sanjid et al., 2016). As a consequence, competition between energy markets with food sectors has caused the increase of edible oil prices. In biodiesel production itself, approximately 70 to 90% of overall biodiesel production cost was accounted solely for feedstock expenditure (Farooq et al., 2013). Therefore, employing cheap raw material in biodiesel production such as waste cooking oil (WCO) is a better option. Utilization of WCO in biodiesel production reduced the cost of production down to 60% in comparison to high-grade

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vegetable oil consumption (Talebian-Kiakalaieh et al., 2013). Due to lack of disposal policy and inefficient waste management, WCO has been directly dumped into sewer and the environment, which led to pipeline blockage and pollution (Mara & Alam, 2008). On top of that, due to its cheap price, some unregulated industries have made profit out of recycling this waste by blending into a new cooking oil product. Thus, based on these issues, it is beneficial to employ WCO as feedstock for biodiesel production.

Transesterification is a process that is involved in biodiesel conversion by detaching 3 free fatty acids (FFA) from a molecule of triglyceride and combining them with alkyl group to form alkyl ester molecules (Sharma et al., 2011). In this process, a homogenous base catalyst, such as sodium hydroxide (NaOH) and potassium hydroxide (KOH), was commonly being used due to its cheap price and high in reactivity (Tariq et al., 2012). Recently, carbon based catalyst has gained attention due to its reusability and high catalytic activity (Konwar et al., 2014). Previously, the development was focused on solid acid catalyst. Nevertheless, since implementation of acid-catalysed reaction was usually associated with impractical procedures such as long reaction time, high amount of alcohol usage, and high temperature condition, solid base catalyst is used due to its benefits such as higher reaction yield, short reaction period, less alcohol usage and conducted at mild reaction condition (Chew & Bhatia, 2008).However, these solid catalysts are expensive that leads to high price of biodiesel. Therefore, development of carbon based catalyst from agricultural waste is gaining interest among researchers due to its low-cost of production (Konwar et al., 2012).

Biodiesel purification step is important in order to improve the quality of the final fuel product in fulfilling the quality specifications standard (EN 14214). The presence of unwanted impurities in biodiesel such as free FFA, free glycerol, catalyst trace, moisture, remaining alcohol and unreacted triglycerides reduced the quality of the fuel (Ngamlerdpokin et al., 2011). Usually, water washing method was applied to purify the crude biodiesel. However, this conventional method produced wastewater at the end of the process, which has to be treated before being discharged (Atadashi et al., 2011; Enweremadu & Mbarawa, 2009). In contrast to purification method using adsorbents, no wastewater are produced and less product loss (Berrios et al., 2011). Activated carbon was recognized as the material with excellent adsorbent properties for purification (Konwar et al., 2014). According to Fadhil et al. (2012), utilization of activated carbon in biodiesel purification produced a better yield and quality compared to conventional water washing method.

Palm oil industry is one of the fast growing economic sectors in Malaysia (Alam, 2008). Increased demand on oil palm led to accumulation of huge amount of biomass waste, such as oil palm empty fruit bunch (OPEFB). As of now, OPEFB was either applied at the plantation as compost fertilizer, burned illegally or act as fuel to generate steam at the mill. Since it was fibrous in structure, this material was considered good for high surface area activated carbon production (Tan et al., 2009).

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The overall objective of this research is to produce heterogeneous catalyst andadsorbent from oil palm biomass for biodiesel production from waste cooking oil. This research also targeted to improve the biodiesel production and purification process in comparison to conventional methods.

1.3 Specific Objectives

1) To produce activated carbon from empty fruit bunch (OPEFB) via two-steps carbonization and chemical activation method.

2) To develop and optimize carbon-supported potassium phosphate tri-basic (K3PO4/AC) catalyst for biodiesel production from WCO.

3) To purify and compare the quality of WCO-derived biodiesel using biomass-derived adsorbent with other purification methods.

1.4 Experimental overview

The overall experimental overview is shown in Figure 1.1. The first objective is on the development of K3PO4/AC catalyst for biodiesel production from waste cooking oil. By using OPEFB as raw material, the catalyst was developed through the process of carbonization, KOH-activation and K3PO4 calcination, consecutively. Subsequently, the prepared K3PO4/AC catalyst was characterized in order to study its physicochemical properties. In transesterification of WCO, the variables affecting the process were optimized in order to determine the highest biodiesel yield. The efficiency of the developed catalyst was also evaluated by conducting reusability and leaching test.

The second objective is to exploit the feasibility of the activated carbon produced from OPEFB biomass in purifying the biodiesel produced from WCO. The quality of the purified biodiesel using the activated carbon was analysed and compared with the conventional water washing method and other commercial adsorbents such as bentonite, silica gel and talc.

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Figure 1.1: Research work flow

Objective 1

Objective 2

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REFERENCES

Adam, I. K., Galadima, A., & Muhammad, A. I. (2011). Biofuels in the quest for sustainable energy development. Journal of Sustainable Development, 4(3), 10–19.

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